I’ll see what I can do, but I guess I have to wait until next year then. A vertical flume flume can be used for this purpose. Yes Zostera marina) seeds are being used in a variety of both small- and large-scale restoration activities and have been successfully used to initiate recovery of eelgrass in the Virginia seaside coastal lagoons, which lost eelgrass in the 1930s ‘wasting disease’ pan-demic (Orth et al. The vertical flume is a low cost construction that produce a vertical flow from the bottom of a tube towards the top. It is possible that the pre-experimental conditions of cold stratification (2 months at 5 °C) influenced the dormancy state at the time of planting. For unsorted seeds, the total seedling emergence was greatest for seeds buried at 0.1–2 cm (48.1–56.7%) and decreased significantly to 12 and 6.2% for seeds buried at depths of 6 and 8 cm, respectively (Fig 1A). 2) Contribute to a field study designed to characterize the flowering phenology of local populations of Zostera marina to determine the appropriate season of seed harvest. This finding suggested the potential of terrapins as seed dispersers in eelgrass beds, which we sampled for two additional years (2010 and 2011). To count the total number of seeds collected, the number of seeds in 1gr could be counted and then multiplied by the total weight of the seeds. Seagrass shoots have been used for restoration with differing degrees of success, but this method has been shown to be expensive and labour intensive. The sediment redox potential was significantly affected by depth (ANOVA; p< 0.001), and decreased to anoxic levels (Eh < 0) at depths below 3 cm, where it remained at a constant level of around -50 mV down to 8 cm depth. To examine the effect of seed size and burial depth on seed germination, seed mortality, seedling emergence, and seedling biomass unsorted seeds were placed at seven different sediment depths (0.1, 1.0, 2.0, 3.0, 4.0, 6.0, and 8.0 cm), and small and large seeds, respectively, were placed at three different depths (2.0, 4.0, and 6.0 cm). Yes After Z. marina seeds were released to water column, all of them were found to fall down on the bottom from the macropodous embryo side. Post hoc analyses of the data was performed with Dunn´s test. This enables subsequent formation of adventitious roots to take place at a position in the sediment that may ensure firm anchorage during the early stage of seedling development [28]. More details on seed storage in Infantes et al (2016a), Planting the seeds at sea is one of the most critical steps. However, with the implementation of EU Directives, no further degradation of coastal habitats will be allowed, and potentially costly measures will be needed to restore degraded valuable coastal environments such as seagrass habitats to a good status. Your email address will not be published. Mean aboveground (A) and belowground biomass (B) of seedlings harvested in July, 2.5 months after experimental start. https://doi.org/10.1371/journal.pone.0215157.t002. Methodology, However, comparable studies of burial limits for Z. marina seeds suggest threshold sediment depths of 5–6 cm [20]. Marine Ecology Progress Series 546: 31-45. Required fields are marked *. The latter are probably very important in the reestablishment of eelgrass beds in denuded areas. Hootsmans et al. Generalized linear mixed model testing the effect of sediment depth on seedling emergence from unsorted seeds, and generalized linear model for effect of depth and seed size on emergence from large and small seed size classes (sorted seeds). At 3–7 days interval, with decreasing frequency as new seedlings ceased to emerge, new seedling were recorded and marked with identification numbers to follow their fate over time. The data consisted of observations of the number of seeds that had emerged at some specified time points, and therefore the exact time at which a seed emerged was unknown, but instead, it was known to have emerged between two consecutive observation times, i.e. The fraction of unemerged seeds that remained viable was significantly affected by seed size, and constituted an overall higher fraction for large (37.2 ± 1.8%) than small (23.1 ± 2.7%) seeds (Fig 1D and 1F, Table 4). Following termination of the experiment, all seedlings were carefully removed from the pots, separated into above- and belowground tissue at the point where the first pair of roots protruded, and dried at 60 °C for 24 h. Unemerged seeds were recovered by sieving the sediment through a 0.6 mm mesh and separated into 1) viable seed, which were intact, hard seeds tested for viability with TTC staining, as described above 2) unsuccessfully emerged seeds defined as seed coats split open and with missing embryo, and 3) dead seeds, which were either soft or failed the TTC staining test. Learn how your comment data is processed. Values are mean ± SE. Various factors may affect the development of sediment seed bank. Cumulative percent of Zostera marina seed germination in the laboratory at 5°C and 15°C with salinities 5, 15, 30 (S5, S15, S30), aeration (A) and no aeration (NA). https://doi.org/10.1371/journal.pone.0215157.g001. In order to improve hypocotyl growth and seed establishment for restorating Zostera marina beds, the postures of seeds on the sea bottom with regard to germination and growth was examined. Ammonium and sulphide can be toxic for aquatic macrophytes even at micromolar concentrations in the water phase [47,48]. Positive effects of burial on early seedling growth and establishment have previously been described for Z. marina [19] and could result from a deeper positioned hypocotyl, increasing the access to sediment nutrient reserves. Funding acquisition, This was followed by a short cooling period until mid-May, where after temperature gradually increased from 13°C to 21°C until mid-august, and then decreased again to 12°C in mid-October when the experiment was finalized. No, Is the Subject Area "Mathematical models" applicable to this article? The high losses of seeds, particularity in shallow areas, as a result of transport by currents, bioturbation and predation, make restoration with seeds inefficient. The fraction of dead seeds was unaffected by time of sampling, but differed significantly between burial depths and was much higher at 6 to 8 cm depth (50.2%) than at 0.1 and 1 cm (17.1 and 23.4%, respectively) (Fig 1C and 1E, Table 4). In this study, seed germination leading to successful seedling emergence occurred at sediment depths down to 8 cm, but increasing seed burial depth severely reduced the number of emerging seedlings and delayed the time of emergence from sediment depths below 3 cm. No specific permission was required to sample eelgrass shoots from this area. Seed burial can be favourable to sexual recruitment, because buried seeds become less accessible to predation [26,27], they are less exposed to removal by water movement, and seedlings may develop root systems with better anchoring capacity, reducing the risk of being dislodged during events of physical stress [28]. With the improvement of conditions, there is a growing interest to restore lost habitats, but methods are lacking for restoration of eelgrass beds at high latitudes where long winters create special challenges. Reproductive shoots bearing nearly-ripe seeds were returned to Gloucester Point, VA, and placed in well-aerated 3,500L flow-through seawater tanks. The coast of the Yellow Sea in China, like many other temperate coastal zones, has been experiencing a dramatic decline in the abundance of seagrass. Eelgrass (Zostera marina) forms the foundation of an important shallow coastal community in protected estuaries and bays.Widespread population declines have stimulated restoration efforts, but these have often overlooked the importance of maintaining the evolutionary potential of restored populations by minimizing the reduction in genetic diversity that typically accompanies … No, Is the Subject Area "Seedlings" applicable to this article? Restoring eelgrass (Zostera marina) from seed: A comparison of planting methods for large scale projects. Similar effect of seed depth on emergence failure has been suggested in a study of Z. marina seed bank dynamics, where the proportion of empty, split seed coats, indicating unsuccessful emergence, was 4 times higher at deep (5 cm) compared to shallow (1 cm) sediment depths [19]. As planting represents a large proportion of the costs associated with restoration, developing cost-effective new planting methods would reduce the costs, and seeds are more practical for large-scale restoration. stenophylla Asch. Other studies have shown that seedling biomass increases with seed mass, and that this may result in higher survival and competitive ability during early seedling establishment [49–51]. Eelgrass (Zostera marina) flowering development and seed production were assessed along a depth gradient at three sites during 2012 and 2013 to 1) describe the flowering seasonality in the Swedish west coast, and 2) evaluate methods using seeds for large-scale restoration, including harvesting, storage and separation of viable seeds using a vertical flume. latifolia Morong: ZOMAS: Zostera marina L. var. Although the success of establishing adults plants fro seeds has been generally low (<10% survival rate), new methods could be investigated to increase the survival rate. Seed burial in eelgrass Zostera marina: the role of infauna Natalia J. Blackburn*, Robert J. Orth Virginia Institute of Marine Science, College of William and Mary, PO Box 1346, Gloucester Point, Virginia 23062, USA ABSTRACT: Seed burial is a vital process that influences small- and large-scale plant population patterns and is frequently mediated by soil-dwelling invertebrates. Zostera marina (eelgrass) is a widespread and often dominant seagrass species in coastal and estuarine ecosystems across the northern hemisphere, where it fulfils important roles as ecosystem engineer and service provider [1,2]. The biomass of seedlings derived from large and small seeds was not significantly affected by seed burial depth at time of sampling (5–6 weeks after peak emergence), but large seeds gave rise to significantly larger seedlings that on average weighed 1.5 times more than seedlings formed by small seeds (Fig 3, Table 5). Funding: This study was supported by the “NOVAGRASS" project (12-132701) funded by the Danish Council for Strategic Research. In mid-August the mature seeds that had settled to the bottom were collected, transferred to mesh bags, and stored in outdoor containers with aerated seawater at in-situ temperatures at Påskehøjgård, Aarhus University (56.22 N, 10.12 E). Along the northwest coast of Sweden, over 50% of Zostera marina L. (eelgrass) meadows have vanished since the 1980s. Software, Software, The maximum potential seed production was greatest at S1 (22228.52 ± 8832.46 seeds ⋅ m –2), followed by S2 (21630.34 ± 9378.67 seeds ⋅ m –2), H2 (7459.60 ± 1779.33 seeds ⋅ m –2), and H1 (2821.05 ± 1280.57 seeds ⋅ m –2). Generalized linear models with the quasi-binomial distribution were used to test for the effect of burial depth and sampling time (June and October) and their interaction on fate of unemerged seeds (viable, dead and unsuccessfully emerged seeds, respectively), and for the effect of seed size (large and small seeds) and burial depth and their interaction on seedling emergence and fate of unemerged seeds. here. Department of Bioscience, Aarhus University, Aarhus, Denmark, Roles However, two recently discovered pathogens of marine plants, Phytophthora gemini and Halophytophthora sp. In addition, sexual recruitment influences population connectivity and contributes to increased genetic variation, which may enhance long-term resilience to stress [10]. https://doi.org/10.1371/journal.pone.0215157.s001, https://doi.org/10.1371/journal.pone.0215157.s002, https://doi.org/10.1371/journal.pone.0215157.s003, https://doi.org/10.1371/journal.pone.0215157.s004. All plants were collected via snorkelling in 1-3m depth. To collect the seeds from the bottom, the flowering shoots were removed and the the bottom of the tank was siphoned with a 4-5 cm diameter hose, since smaller hoses can get easily clogged with leaf debris. Water temperature was recorded every 30 min by HOBO temperature loggers (U22-001) placed in each tank at the start of the experiment. Eelgrass (Zostera marina L.) seed protection for field experiments and implications for large-scale restoration Study on Zostera marina L. Seed Germination Ecological Characteristics in Variable Environmental. Citation: Jørgensen MS, Labouriau R, Olesen B (2019) Seed size and burial depth influence Zostera marina L. (eelgrass) seed survival, seedling emergence and initial seedling biomass development. A portion of the seeds was then sorted by eye into batches of large and small seeds. Investigation, This finding suggested the potential of terrapins as seed dispersers in eelgrass beds, which we sampled for two additional years (2010 and 2011). To collect the seeds from the bottom, the flowering shoots were removed and the the bottom of the tank was siphoned with a 4-5 cm diameter hose, since smaller hoses can get easily clogged with leaf debris. Ten species, including crustaceans, molluscs and fish, were examined for predacious activity onZostera marina L. seeds and seedlings. The arrow indicates when fertilizer was added to two treatments (sand + fertilizer; estuarine sediments + fertilizer). No, Is the Subject Area "Hypocotyl" applicable to this article? After the seeds ripened, the plant material was Total seedling emergence was quantified as the cumulated percentage of emerged seedlings at the end of the experiment. While clonal growth is the principal mode for sustaining persistent meadows, sexual recruitment plays a vital role in population expansion and recovery, and is necessary for the colonization of areas outside the range of vegetative growth [6–9]. The goal of this work was to determine the role that benthic infauna play in the burial of Z. marina seeds by addressing the following questions: 1. The rate and percentage of seedling emergence with increased seed burial depth did not strictly reflect seed size. Seeds of Zostera marina (eelgrass) can be used for restoration if they are available. More details of this methodology and data in (Infantes et al 2018), After harvesting, flowering shoots can be stored in tanks on land until seeds naturally drop from the spathes. The fraction of unsorted seeds that germinated but did not successfully emerge, as indicated from the number of empty, split seed coats, was unaffected by seed burial depth and time after planting (2 and 6 months), and constituted a small fraction of 8.0 ± 1.3% of total planted seeds across all seed burial depths (Fig 1C and 1E, Table 4). Sexual recruitment in plant populations is a multi-stage sequential process and is the combined result of seed production and dispersal, and the prevailing environmental conditions at the time of dormancy relief, germination and seedling emergence [11]. Seedling emergence, defined by the emergence of the cotyledon at the sediment surface, was followed from 23 April and until the pots were destructively sampled on 26 June and 15 October for the two series of pots with unsorted seeds, respectively, and on 5 July for pots with large and small seeds. While moderate burial generally is considered advantageous for seedling recruitment, seeds located on the sediment surface germinate slower [17] and are more vulnerable to losses caused by export to unfavourable sites, uprooting due to poor anchorage [28] and predation [26,27]. The best conditions for storing Zostera marina seeds in Sweden is at temperature of 4oC and a salinity of 32. This may have increased the germinability of the seeds upon transfer to experimental conditions, thereby activating embryo metabolism leading to reduced seed persistence to the chemical environment at depth. Post hoc comparisons between treatments were performed with pairwise comparisons. Resources, Zostera marina (eelgrass) (Figure 1). Seeds will accumulate in the bottom of the tanks until they are collected. The It is in flower from June to September, and the seeds ripen from August to October. However, relatively little is known about the fate of buried seeds and their ability to emerge from greater depths. Seagrass restoration can be performed with seedlings and seeds. Statistical inference for the total seeding emergence from unsorted seeds was made using binomial quasi-likelihood methods (i.e. Europe is presently not prepared for this challenge since effective measures halt the ongoing decline and restore degraded habitats is largely missing. Rank Scientific Name and Common Name; Kingdom: Plantae – Plants Subkingdom: Tracheobionta – Vascular plants Superdivision: Spermatophyta – Seed plants Division: Magn Sammanfattning. The initial discovery in May 2009 of eelgrass (Zostera marina) seeds in fecal samples of wild-caught northern diamondback terrapins (Malaclemys terrapin terrapin) was the first field evidence of eelgrass seed ingestion in this species. https://www.eduardoinfantes.com/pubs/eelgrass-seed-harvesting-coastal-restoration-sweden/. One-way ANOVA testing the effect of seed burial depth on the biomass (mg DW seedling-1) of seedlings emerging from unsorted seeds two (June) and six (October) months after planting, respectively, and two-way ANOVA testing the effect of seed burial depth and seed size on seedlings emerging from small and large seed-size classes (sorted seeds). Seeds have an important role in the reproduction of seagrasses, such as Zostera marina and Cymodocea nodosa, and using seeds to repair damaged meadows has resulted in faster recovery than transplanting plants . To estimate sediment organic content, samples dried at 105 °C until constant weight were combusted at 550 °C for 24 hours and weight loss was calculated. Seed size was measured on 100 seeds with natural size distribution (unsorted seeds hereafter) and on 30 seeds from the batches of large and small seeds (sorted seeds hereafter), respectively. ( sand + fertilizer ) methods ( i.e … seed - best sown as soon as it is ripe loggers... 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